Effect of UV irradiation on the aggregation of TiO2 in an aquatic environment: Influence of humic acid and pH

2016 ◽  
Vol 212 ◽  
pp. 178-187 ◽  
Author(s):  
Peifang Wang ◽  
Ning Qi ◽  
Yanhui Ao ◽  
Jun Hou ◽  
Chao Wang ◽  
...  
2012 ◽  
Vol 724 ◽  
pp. 33-36 ◽  
Author(s):  
Jong Oh Kim ◽  
Seung Pil Choi ◽  
Geon Tae Kim ◽  
Yong Hak Kim

We evaluated the treatment efficiency of humic acid using Ti and anodized TiO2metal plate with/without Fe-doping. Variation of humic acid concentration after 60 minutes of UV irradiation in the case of Ti only, Fe-Ti, TiO2only and Fe-TiO2was about 3.0%, 5.5%, 9.8% and 9.2%, respectively. . It is found that hypochromic effect was revealed in all cases with respect to doping time. Fe doping method is considered to be effective for humic acid degradation in spite of relatively low surface area of Ti and anodized TiO2metal plate.


Chemosphere ◽  
2020 ◽  
Vol 244 ◽  
pp. 125582 ◽  
Author(s):  
Chao Song ◽  
Hua-Yu Liu ◽  
Shuang Guo ◽  
Shu-Guang Wang

Nanomaterials ◽  
2017 ◽  
Vol 7 (10) ◽  
pp. 326 ◽  
Author(s):  
Cheng Peng ◽  
Chensi Shen ◽  
Siyuan Zheng ◽  
Weiling Yang ◽  
Hang Hu ◽  
...  

Membranes ◽  
2019 ◽  
Vol 10 (1) ◽  
pp. 3 ◽  
Author(s):  
Sungju Hwang ◽  
Yooju Lee ◽  
Jin Yong Park

Photooxidation oxidizes most organic compounds by mineralizing them to small inorganic molecules. In this study, the effects of dissolved organic matter (DOM), pH, and polypropylene (PP) beads concentration on membrane fouling were investigated in a hybrid water treatment process consisting of seven-channel alumina microfiltration (pore size 1.0 μm) and pure PP beads water backwashing with UV irradiation for photooxidation. The synthetic feed was prepared with humic acid and kaolin and flowed inside the microfiltration (MF) membrane. The permeate contacted the PP beads fluidized in the gap of the membrane and module with outside UV irradiation. Membrane fouling resistance (Rf) increased dramatically with an increase in the concentration of humic acid (HA) from 6 mg/L to 8 mg/L. The treatment efficiency of DOM increased dramatically, from 14.3% to 49.7%, with an increase in the concentration of HA. The Rf decreased with an increase of PP beads concentration. However, maximum permeate volume (VT) was acquired at 5 g/L of PP beads. The maximal treatment efficiency of DOM was 51.3% at 40 g/L of PP beads. The Rf increased with an increase in the pH of feed, and the maximum VT was acquired at a pH of 5. The maximal treatment efficiency of DOM was 52.5% at pH 9.


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